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Diss Factsheets
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EC number: 700-777-2 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- other: Expert review and assesment
- Adequacy of study:
- supporting study
- Reliability:
- other: Not assignable as result is from expert asessment.
Data source
Reference
- Reference Type:
- other: Internal Company Report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Assessment of toxicokinetic behaviour of the substance derived from available data as required by REACH Annex VIII section 8.8
- Deviations:
- not applicable
- Principles of method if other than guideline:
- Expert review.
- GLP compliance:
- no
Test material
- Reference substance name:
- Automatically generated during migration to IUCLID 6, no data available
- IUPAC Name:
- Automatically generated during migration to IUCLID 6, no data available
- Test material form:
- other: tudy undertaken as expert review of available data which is based on test material in powder form.
Constituent 1
Results and discussion
Any other information on results incl. tables
INFORMATION BASED ON PHYSICO-CHEMICAL PROPERTIES
The test substance is a lithium salt of a phthalonitrile derivative with a molecular weight of 320 as the lithium salt. It is an involatile solid at room temperature and has a melting point of > 300°C. The substance is very soluble in water (> 25% w/w at 25°C). The log Powis -3.09 suggesting that the substance is of very limited solubility in lipids.
In its solid form the test substance is a fine powder of which 52.4% of the particles are inhalable (particle size <100 µm) and 4.39 x 10-2% are respirable (particle size < 5.5 µm).
The test substance is hydrolytically stable at pH 4 and pH 7 at 50°C giving an estimated half-life of > 1 year at 25°C, however, at pH 9 it undergoes rapid hydrolysis and shows 99.5% hydrolysis after five days at 50°C. Two main hydrolysis products are produced which are believed to bestructurally similar to the test substance.
ABSORPTION, DISTRIBUTION AND EXCRETION
Absorption
Potential for Absorption
The test substance in solid form contains 52.4% particles of a size that could be inhaled following exposure to airborne dusts. However as < 0.1% of particles are respirable, little of an in haled dose will reach the alveoli and most of the dose can be expected to be transferred to the stomach via mucocilliary action and swallowing.
The test substance is a relatively low molecular weight molecule and therefore its size is unlikely to present a significant barrier to absorption across the gastrointestinal mucosa, hence, uptake as it passes through the gastrointestinal tract may occur. Uptake is likely to vary as it passes through the gut given that it will be ionised to differing degrees at the different pH’s encountered in the gastrointestinal tract. The test substance has a very low log P value and therefore the unionised form is likely to be inhibited from passage across membranes due to a lack of lipid solubility. It is unlikely that active transport mechanisms will be a significant uptake route due to a lack of similarity with endogenous molecules; however, the test substanceis a salt and will release lithium ions which will compete with sodium ions for uptakevia sodium pumps.
Overall, it can be expected that absorption of the intact molecule across the gastrointestinal mucosa will occur, but a proportion of an oral dose is likely to not be absorbed and subsequently be excreted in the faeces.
The test substance undergoes limited hydrolysis at pHs of 4 and 7 with less than 10% hydrolysis occurring after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C. However, at pH 9 after 5 days at 50 °C almost 100% hydrolysis occurs. Based on the hydrolysis results, it is possible that following oral administration, at least a degree of hydrolysis of the test substance might occur in the lower intestine where up toca.pH 8 could be encountered.
The hydrolysis products are expected to be less lipophilic than the test substance which may alter the absorption profile; however, given the structural similarity of the products to the test susbtance, it is expected that overall they will have a similar absorption profile to the parent molecule.
Evidence for Absorption
An oral repeated dose reproductive developmental toxicity screening study has been conducted on the test substance using doses of 30, 300 and 500 mg/kg/bw/day. Some transient treatment related effects were seen at 500 mg/kg/bw/day such as impairment of body weight in both sexes along with minimal disruption in blood chemistry in females. There was also a nominal effect on adrenal weight in all treated females that may have had an associated histopathological relationship. These findings were not considered toxicologically significant; however, they do provide evidence that the test substance and/or its metabolites/hydrolysis products can be absorbed to a degree sufficient to exert effects.
There is no information on which to determine for certain whether the test substance can be absorbed significantly via dermal exposure. Given its molecular weight it is conceivable that a dermal absorption could occur; however, factors such as it low lipid solubility are likely to mean that absorption by this route is unlikely to be significant.
DISTRIBUTION
It is very unlikely that the test substance will exhibit any significant distribution within the body between plasma and tissues. The substance is a salt and on dissolution will form an anion and a lithium cation. The anion is polar and therefore it is unlikely to distribute to any significant extent in the body. The lithium cation is likely to compete with sodium for uptake via sodium pumps and ultimately it is likely to be incorporated into the body sodium pool. If not replenished, the lithium will be lost over time via normal excretion processes.
As no reproductive effects were seen in the oral repeated dose reproductive developmental toxicity screening study it is not possible to draw any conclusions about whether the distribution of the test substance in the body can include the reproductive organs.
METABOLISM
The test substance contains a water solubilising sulphonic acid and two cyano groups which are likely to aid metabolism of the molecule by the cytochrome P450 enzyme metabolising system. The sulphonic acid group is also likely to aid excretion of the molecule.
In an in vitro bacterial reverse mutation assay using S. typhimurium and E.coli the test substance did not induce any significant increases in observed numbers of revertant colonies. The test substance gave a negative result in an in vivo Mouse Micronucleus Test. Given the negative results, no conclusions about the potential of the test substance to undergo metabolic change can be drawn from these studies.
In an in vitro mammalian chromosome aberration assay in human lymphocytes, the test substance was considered to be clastogenic following 24-hours of continuous exposure in the absence of metabolic activation (rat liver homogenate (S9)). It was negative in the presence of S9 and this may indicate that the test substance can undergo metabolism in the liver and possibly other organs.
Excretion
The main route of excretion of absorbed test substance and/or its metabolites is likely to be via the kidneys into the urine. The molecular weight of the test substance is below the biliary exclusion limit of circa 325 in the rat and 500 in humans and therefore elimination of any absorbed substance in the bile is not expected to be significant.
The lithium ions from the test substance can be expected to be excreted in urine.
CONCLUSION
An assessment of the potential absorption of the test substance based on its physico-chemical properties suggest that absorption across thegastrointestinal mucosa is likely to be slow and part of an oral dose can be expected to be excreted in the faeces. However, a proportion is systemically absorbed as demonstrated by the observation of transient treatment related effects in a repeated dose reproductive developmental toxicity screening study.
There is evidence that the test substance can be metabolised by liver S9. The presence of sulphonic acid and cyano groups on its structure can be expected to aid metabolism of systemically, absorbed test substance to water soluble products that will ultimately be excreted via the kidneys. There is no expectation that the test substance will preferentially distribute to particular organs or tissues in the body.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): other: No bioaccumulation potential based on expert review of available data.
A proportion of the test substance is likely to be systemically absorbed but likely to be subject to metabolism via sulphonic acid and cyano groups on its structure. Ultimately, it is expected to be excreted via the kidneys. There is no expectation that the test susbstance will preferentially distribute to particular organs or tissues in the body. - Executive summary:
Introduction
An expert review of the toxicokinetic profile of the test substance was undertaken based on physicochemical profile and available toxicity data.
Conclusion
An assessment of the potential absorption of the test substance based on its physico-chemical properties suggest that absorption across thegastrointestinal mucosa is likely to be slow and part of an oral dose can be expected to be excreted in the faeces. However, a proportion is systemically absorbed as demonstrated by the observation of transient treatment related effects in a repeated dose reproductive developmental toxicity screening study.
There is evidence from an in vitro mammalian chromosome aberration test that the test substance can be metabolised by liver S9. The presence of sulphonic acid and cyano groups on its structure can be expected to aid metabolism of systemically, absorbed test substance to water soluble products that will ultimately be excreted via the kidneys. There is no expectation that the test substance will preferentially distribute to particular organs or tissues in the body.
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